(1) This Procedure applies to all workers at The University of Queensland (UQ) who generate radioactive waste through their activities and provides advice on the processes required to ensure compliance with Part 5 of the Radiation Safety Act 1999 and Part 4 of the Radiation Safety Regulation 2021 to ensure user and public safety and to prevent environmental contamination. (2) This Procedure details how the following types of radiation waste will be managed at UQ: (3) All radioactive waste procedures for facilities will be specified in the relevant approved Radiation Safety and Protection Plan (RSPP). (4) The Procedure should be read in conjunction with other Radiation Safety procedures and guidelines. (5) For the management of radiation waste, the following requirements must be observed: (6) The management of radioactive waste must include the regular disposal of the waste, and planning for ongoing removal of the waste must occur and the Organisational Unit must budget for at least annual removal of radioactive waste. This requirement must be included in the RSPP. Users must dispose of radioactive waste as required and record any disposal in the register of radioactive waste (see clause 41). (7) There are requirements for disposing of different types of radiation sources as waste: (8) There are essentially two ways of managing unsealed radioactive wastes: (9) While the latter option is appropriate for materials associated with the nuclear fuel cycle, it is not required for the relatively low radiotoxicity substances used for research in the biological sciences or most other research fields at UQ. (10) Radioactive wastes can generally be disposed of safely by dilution to very low concentrations prior to release. This is recognised by international bodies and acceptable concentrations of most isotopes are specified in the Regulation. (11) The legislation provides for two ways in which radioactive material can be disposed of: (12) The physical nature of the waste determines to a significant degree the actual disposal procedures to be adopted: (13) The Regulation allows for disposal of radioactive material to the sewerage system provided the concentrations are below scheduled limits in the Regulation. (14) Maximum concentration or activity levels vary depending on the radionuclide and how the radiation source is being disposed of: (15) In disposing of water-soluble liquid waste to the sewer, precautions are required to prevent splashing or aerosol formation which could spread contamination or create a respirable fraction. Best practice is the use of “flushing rim” laboratory sinks which allows flushing with known volumes of water while minimising splashing. (16) If flushing rim sinks are not available then standard (or deep) conventional laboratory sinks can be used to dilute and flush liquid waste so long as suitable arrangements (e.g., decreasing the water flow rate, using anti-splashing water tap) are made to prevent splashing and to allow for the gradual flow of waste liquid into a stream of water as it runs to waste. (17) Requirements for the maximum concentrations of radioactive substances allowable in wastewater that flows to a sewer main are given in Column 4 of Schedule 3 of the Regulation. UQ licensees must consider the concentration limits as applying to their individual laboratories. (18) Solvent waste cannot be disposed of in general waste streams due to their hazardous properties, even where the radioactive content is insignificant. Consequently, solvent waste must be collected in drums according to solvent type and then disposed of as a hazardous chemical. (19) The Regulation requires the concentration of a radionuclide in waste (other than where the waste is disposed of into the air, water or a sewer system) to be less than half the concentration given in Column 2 of Schedule 1 in the Regulation. (20) The radioactive content of the scintillant waste can be assessed by counting a sample in a liquid scintillation counter with automatic quench correction. Concentrations in disintegrations per minute (dpm) per litre can be converted to becquerels per litre by dividing by 60. (21) It is important not to mix scintillants containing different radionuclides as this would make activity assessment difficult including decay times. (22) The concentration in most scintillant waste is likely to be well below the level of prescription although some may require storage for decay or additional dilution. In most cases, dilution is not needed. If it has be diluted, the UQ Science Store should be contacted for further guidance – to see if same solvent (waste) is available. (23) Where solvents have to be stored for decay, they must be appropriately stored in line with the Chemical Storage Safety Procedure and labelled (refer to Chemical Labelling Procedure) with details of the contents, including: (24) Flammable solvents must be stored in accordance with the requirements outlined in the Flammable and Combustible Liquids: Storage and Handling Procedure. (25) The Regulation requires the concentration of a radioisotope in waste (other than where the waste is disposed of into the air, water or a sewer system) be less than half the concentration given in Column 2 of Schedule 1 in the Regulation. (26) Short lived solid wastes (e.g., those with half-lives of less than a few months) must be retained within appropriate plastic bags (shielding may be required) in the laboratory or dedicated storage room until the radioactivity has fallen to exempt levels under the Regulation. (27) The person who creates the waste must make an assessment of the activity present in materials such as discarded and contaminated lab consumables that form the bulk of solid wastes from laboratories. While a survey meter can be used to detect the presence of radioactivity, attenuation by packaging material and irregular source geometry can lead to substantial underestimation of the amount of active material present. If there is any uncertainty, the package must be stored for a longer period. (28) With Tritium and Carbon 14, the amounts packaged for disposal must be within the guidelines as there will be no appreciable decay of activity over practical time spans. (29) Solid waste being stored for decay must be labelled with: (30) Areas in which wastes are stored for decay must be appropriately signed and access controlled. The storage room requires certification by an accredited person every five years to ensure the safety and compliance according to Radiation Safety Standard 2021. (31) Solid waste, empty packaging or containers which once contained radioactive materials must be checked with an appropriate meter to confirm any contamination. Uncontrolled disposal may occur where solid waste and empty packaging have a sufficiently low activity concentration (refer to schedule 3 of the Regulation) and have no other hazardous properties. They must not bear any radioactive or other warning labels when being disposed of. (32) The disposal of disused sealed radioactive substances is different from liquid and solid radioactive waste. Generally, there are two disposal methods which are practically feasible for UQ workers. (33) The preferred strategy is to return the source to the supplier or manufacturer. This request can be done at any time but ideally this requirement is included in the purchase contract indicating the sealed source(s) will be returned to the supplier or manufacturer when disused, with or without extra cost, before the contract is signed. The other is to gain a disposal approval from Queensland Radiation Health. (34) There may be cases in which the nature of the waste or the proposed method of disposal do not fit clearly into the categories set out in the Regulation. In these circumstances, an application for Approval to Dispose of radioactive material is required. (35) The assistance of the Radiation Protection Consultant (RPC) should be obtained where the need for such an application arises. (36) Disposal of radiation apparatus, requires: (37) Radioactive waste must be stored in appropriate containers. For example, left-over radioactive material must be kept in the original container; contaminated items such as gloves stored in plastic bags; large quantities of liquid stored in glass containers after taking chemical safety into account (refer to Chemical Storage Safety Guideline). (38) All stored radioactive waste must be labelled with radiation warning signs and the following information where possible: radioisotope(s), activity and date of measurement. (39) Radioactive waste must be stored securely in a storage area or room. Access should be given only to authorised persons. The name and contact number of the local RSO must also be displayed on the wall or door. (40) Storage area or room must be certified by an accredited person every five years to ensure the compliance with Radiation Safety Standard 2021. (41) This register is a central shared document, e.g., via MS Teams, that is maintained and kept up to date by the RSOs and RPC. The Organisational Unit RSO will update the register when radioactive waste is disposed of or added. In addition, for nuclear material regulated by the Australian Safeguards and Non-Proliferation Office (ASNO), an ASNO database must be updated by RPC annually. (42) The RSO for each radiation practice must audit the storage of radioactive waste at least every six months and make a record of such that includes information on – quantity of waste stored matches that recorded in the register of radioactive waste, the waste is securely stored with access restricted, the waste is stored such that it is not a risk to people, property or the environment, that plans and budget are in place to safely dispose of the waste ongoingly in order to prevent a build-up of legacy radioactive waste. (43) For the disposal of nuclear material regulated by ASNO, an application must be submitted by the RPC and the approval from ASNO must be in place prior to the disposal. (44) The RSPP for each radiation apparatus or radiation source associated with a radiation practice must specify how associated radiation waste will be disposed of and how often. (45) UQ has been granted three Possession Licences for the radiation sources under the Act. The Possession Licensee is responsible for ensuring compliance with both the legislation and specific licence conditions. (46) The Possession Licensee can nominate a nominee to carry out activities on their behalf and this can be any Senior Executive member. To be nominated, the Senior Executive member must contact the Health, Safety and Wellness Division (HSW Division) so the process can be completed and QRH be informed of the nomination. (47) The Nominee’s responsibilities, which can be delegated to Executive Deans, Institute Directors or Heads of School, are as follows: (48) The Act requires each Possession Licensee to appoint a qualified RSO. The RSO is required to: (49) The RPC provides overall guidance to all UQ workers on matters pertaining to radiation. The RPC monitors the implementation of UQ’s RSPPs as approved by the regulatory authority, provides support for radiation governance and compliance across UQ and monitors compliance with radiation safety legislation. (50) The RPC is the primary source of advice and expertise for: (51) In addition, the RPC provides reports regularly via the Director of the HSW Division, to Possession Licence nominees about any issues or changes that may affect the Possession Licence. (52) The primary responsibilities of a user are to: (53) Health, Safety and Wellness Division (HSW Division) is responsible for maintaining the required level of central oversight and assurance by: (54) This is a formal network of UQ RSOs. The forum allows the RPC and RSOs to consult on, and review regulatory, organisational and technical radiation matters at UQ. (55) The RSO Network meets four times a year and is chaired by the RPC. All participants are invited to contribute discussion and presentation items for the meeting. The RSO community provide secretariat duties as needed. All presentations and minutes are retained by HSW Division. (56) The RPC oversees radiation safety arrangement at UQ and reviews the specific aspects of radiation safety regularly. Local RSOs communicate radiation safety issues to the RPC as required. (57) Local RSOs must ensure a: (58) For each disposal operation, a record should include:Management and Disposal of Radioactive Waste Procedure
Section 1 - Purpose and Scope
Section 2 - Process and Key Controls
Top of PageSection 3 - Key Requirements
Management of Radioactive Waste
Liquid Radioactive Waste
Water-soluble Materials
Required Dilutions
Organic Solvent Wastes
Management of Solid Radioactive Waste
Disposal Procedures for Solids and Packaging
Disposal of Disused Sealed Radioactive Substances
Disposal Approvals
Disposal of Radiation Apparatus
Radioactive Waste Storage
Storage Containers
Radioactive Waste Storage Area or Room
Register of Radioactive Waste
Audit of Radioactive Waste Storage
Disposal of Nuclear Material Regulated by ASNO
Radiation Safety and Protection Plan (RSPP)
Section 4 - Roles, Responsibilities and Accountabilities
Possession Licensee
Nominee
Radiation Safety Officer (RSO)
Radiation Protection Consultant (RPC)
User
Health, Safety and Wellness Division
Radiation Safety Officer Network
Section 5 - Monitoring, Review and Assurance
Records of Radioactive Waste Disposal
Top of PageSection 6 - Appendix
Definitions
Term
Definition
Accredited Person
An individual with skills, knowledge and experience in assessing particular radiation sources or premises where they are used or stored for compliance with radiation safety standards. A person who has an Accreditation Certificate is allowed to issue Certificates of Compliance for the types of radiation sources or premises detailed in their certificate. A list of accredited person can be found on QRH website.
Nuclear Material
Uranium, plutonium, and thorium, in any form, consisting of natural and depleted uranium, or enriched uranium, uranium-233, and plutonium-239.
Radiation Protection Consultant (RPC)
A qualified expert appointed by the responsible person to supervise radiation safety activities and to ensure radiation safety. An PRC is deemed to have the authority to implement procedures and to intervene in situations where safety has been or is being compromised.
Radiation Safety Officer (RSO)
For a radiation practice, means a person who holds a relevant certificate issued under the Act and who the possession licensee nominee has appointed as the Radiation Safety Officer for the particular practice.
Radiation Safety and Protection Plan (RSPP)
Is the risk management plan for a particular type of radiation practice. The relevant RSPP must be complied with by all users and other persons involved in the practice.
UQ Workers
For the purposes of this Procedure includes:
• staff - continuing, fixed-term, research (contingent funded) and casual staff;
• contractors, subcontractors and consultants;
• visiting academics and researchers;
• academic title holders, visiting academics, emeritus professors, adjunct and honorary title-holders, industry fellows and conjoint appointments;
• higher degree by research students;
• volunteers and students undertaking work experience.
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